harmonisation of exposure and risk assessment models for the benekempen project griet van gestel
DESCRIPTION
Harmonisation of exposure and risk assessment models for the BeNeKempen project Griet Van Gestel OVAM. Co-authors:. Van Gestel Griet 1 , Cornelis Christa², Kuppens Carla³, Swartjes Frank 4 1 OVAM Public Waste Agency of Flanders - Department of Soil Management – Belgium - PowerPoint PPT PresentationTRANSCRIPT
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Harmonisation of exposure and risk assessment models for the
BeNeKempen project
Griet Van Gestel OVAM
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Co-authors:
Van Gestel Griet1, Cornelis Christa², Kuppens Carla³, Swartjes Frank4
1 OVAM Public Waste Agency of Flanders - Department of Soil Management – BelgiumStationsstraat 110, B-2800 Mechelen, , tel.: ++32/15.284.493 ² VITO Flemish Institute for Technological Research – Belgium ³ ABdK – Active Soil Management Campine area– The Netherlands 4 RIVM National Institute of Public Health and the Environment – The Netherlands
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Content :
1. The BeNeKempen project
2. Approach to harmonization
3. Examples
4. Conclusions
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1. The BeNeKempen project
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1. The BeNeKempen project (1/5)
The NO part of Belgium and the SE part of the Netherlands (Campine area)
End 19th century - 1970’s: non-ferrous industries:emissions, discharges of waste water, use of ashes for pavement of roads
diffuse soil contamination contamination of sediments,
groundwater and surface water
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1. The BeNeKempen project (2/5)
Similar problems at both sides of the border:- human health and ecological risks;- hindrance of different activities: e.g. roadworks on roads paved with ashes, dredging of rivers, ...
BeNeKempen project
Partners: OVAMABdK
with financial support EU INTERREG III
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1. The BeNeKempen project (3/5)
Objective of the BeNeKempen project:to develop and implement cross-border strategies to solve problems related to the heavy metal contamination and to reduce risks
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1. The BeNeKempen project (4/5)
One aspect: to assess and manage human health risks
But: different guidelines and methodologies for risk assessment in the two countries
different conclusions for the same contamination with regard to risks
Difficult to explain!
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1. The BeNeKempen project (5/5)
One of the aims of the project:to develop a common methodology for risk assessment for soil contamination in the Campine area
by harmonizing regional (Flanders) and national (The Netherlands) methodologies
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Content :
1. The BeNeKempen project
2. Approach to harmonization
3. Examples
4. Conclusions
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2. Approach to harmonization (1/4)
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2. Approach to harmonization (2/4)
Standard-computing models: to calculate transfer of contaminants and exposure
dosis, and assess risks
in Flanders: Vlier-humaan in the Netherlands: CSOIL
similar basis, but many input parameters differ
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2. Approach to harmonization (3/4)
Selection of relevant aspects: contaminants: Cd, Pb, As land use scenarios:
– vegetable garden– residences with garden– residences without garden– recreation
exposure routes:– ingestion of soil and dust– inhalation of soil and dust– consumption of vegetables– consumption of drinking water
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2. Approach to harmonization (4/4)
Inventory of differences: description of algorithms and parameters in
Vlier-humaan and CSOIL analysis
Discussion leading to consensus: straightforward
more research
policy decisions
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Content :
1. The BeNeKempen project
2. Approach to harmonization
3. Examples
4. Conclusions
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3. Examples (1/7)
Uptake by plants
Soil ingestion rates
Background exposure (air and food)
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3. Examples (2/7)
Uptake by plants:
Vlier-humaan and CSOIL:
Cplant = BCF * Csoil
Analysis:BCF’s soil characteristics
plant species
e.g. Cd, carrots (Flanders):
log BCF = 0.54 - 0.12 * pH-KCl - 0.75 * log Csoil
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3. Examples (3/7)
Uptake by plants:
Harmonization:
grouping of data from the Netherlands and Flanders
e.g. Cd, carrots:
log BCF = 0.43 - 0.12 * pH-KCl - 0.51 * log Csoil
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3. Examples (4/7)
Soil ingestion rates:
CSOIL: no distinction inside/outsideVlier-humaan: distinction inside/outside
mg/ dag children adultsCSOIL residential recreation
15030
5010
Vlier-humaan residential recreation
50100
2050
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3. Examples (5/7)
Soil ingestion rates:
Analysis: uncertain, few experimental dataliterature research
Harmonization:common values for amount/day
mg/ dag children adultsHarmonization residential recreation
100130
5050
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3. Examples (5/7)
Soil ingestion rates:
Harmonization:preliminary results
more research data needed:- intake inside / outside- concentration of metals in soil taken in- land use type: urban / rural- validation e.g. biomonitoring
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3. Examples (6/7)
Background exposure (air and food):
CSOIL: noVlier-humaan: yes
Analysis: different viewpoints:
with background: protection of people, whole environment is considered
without background: only soil pollution is considered
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3. Examples (7/7)
Background exposure (air and food):
Harmonization: stepwise approach clarify importancewith background exposurewithout background exposure
e.g. critical values for residences with garden
mg/ kg ds with BG without BG
As
Cd
Pb
63
42
560
154
63
612
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Content :
1. The BeNeKempen project
2. Approach to harmonization
3. Examples
4. Conclusions
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4. Conclusions (1/2)
harmonization of methodologies is possible by introducing most recent developments
research needs are indicated, research is ongoing, methodology will be adapted
policy decisions different options were calculated in order to clarify
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4. Conclusions (2/2)
need for harmonisation of methodologies for risk assessment on a larger scale
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Thank you for your attention